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Eur. J. Entomol. 109: 527–534, 2012
http://www.eje.cz/scripts/viewabstract.php?abstract=1738
ISSN 1210-5759 (print), 1802-8829 (online)
Inhabiting warm microhabitats and risk-spreading as strategies for survival
of a phytophagous insect living in common pastures in the Pyrenees
GREGOR STUHLDREHER1, LUIS VILLAR2 and THOMAS FARTMANN1*
1
Department of Community Ecology, Institute of Landscape Ecology, University of Münster, Robert-Koch-Straße 28,
48149 Münster, Germany; e-mails: gregor.stuhldreher@uni-muenster.de; fartmann@uni-muenster.de
2
Instituto Pirenaico de Ecología, IPE-CSIC, Apdo. 64, 22700 Jaca (Huesca), Spain; e-mail: lvillar@ipe.csic.es
Key words. Lepidoptera, Lycaenidae, Satyrium spini, oviposition, batch size, conservation management, grazing, microclimate
Abstract. The breakdown of the transhumant grazing system in the Spanish Pyrenees has led to a severe decline in the area of pastures. However, in the high mountain zone there are still large areas of species-rich grasslands. The aim of this study was to assess
the oviposition preferences of the shrub-feeding Blue-spot hairstreak, Satyrium spini (Denis & Schiffermüller, 1775), in montane
common pastures in the Spanish Pyrenees and recommend a way of managing these grasslands that favours this species. Our study
showed that females of S. spini laid their eggs on Dwarf buckthorn (Rhamnus pumila Turra) and Alpine buckthorn (R. alpina L.),
which are novel host plant records for Spain. A warm microclimate was of crucial importance for egg-laying. Occupied plants grew
mostly at sparsely vegetated grassland sites where there were large patches of bare rocks, stones or gravel. Most egg batches were
laid close to the ground and 75% consisted of only one egg. The number of batches per R. pumila plant was higher on east-, southand west-facing slopes than on north-facing slopes. Presence of eggs and the number of egg batches per R. pumila plant were best
explained by a long sunshine duration. At high altitudes particularly warm microhabitats seem to be more important for S. spini than
at lower altitudes in Central Europe. We assume that the preference for unusually warm microhabitats is explained by the cold climatic conditions near the altitudinal range limit of the species. That most of the eggs were laid singly and not in small batches as in
Central Europe might be a risk-spreading strategy to cope with the harsh climatic conditions and the high inter-annual variation in
weather conditions in the high mountain zone in the Pyrenees. The best way to maintain open grasslands for S. spini and other thermophilous grassland species in the high mountain zone of the Pyrenees is to use the traditional combination of sheep and cattle grazing.
INTRODUCTION
During recent decades, the worldwide rate of species
extinctions has risen continuously and is now estimated to
be 100 to 1000 times higher than the natural background
extinction (Pimm et al., 1995). In terrestrial ecosystems,
the most important driver of this process is land-use
change (Sala et al., 2000). On a global scale it is expected
to have the largest impact on biodiversity by the year
2100 and to be even more important than other factors
like climate change or nitrogen deposition.
The transition from traditional land-use to modern agriculture mostly entails two contrasting processes: intensified use of productive sites that can be cultivated
mechanically and abandonment of marginal land (Foley
et al., 2005; Henle et al., 2008; Kleijn et al., 2009). Both
phenomena often have adverse effects on species
richness. Intense exploitation of agricultural land occurs
mainly in lowlands with fertile soils and sufficient rainfall
or irrigation water, whereas abandonment of land is
typical of mountain areas (Caraveli, 2000; MacDonald et
al., 2000). Declines in habitat and species diversity due to
cessation of traditional land use have been reported for
several European mountain ranges (MacDonald et al.,
2000; Tasser & Tappeiner, 2002; Bezák & Halada, 2010).
The causes and consequences of land-use change are
particularly well studied in the Spanish Pyrenees (GarcíaRuiz & Lasanta-Martínez, 1990; García-Ruiz et al., 1996;
Poyatos et al., 2003; Lasanta-Martínez et al., 2005;
Vicente-Serrano et al., 2005). The traditional agricultural
systems have undergone dramatic changes since the
beginning of the 20th century (García-Ruiz & LasantaMartínez, 1990; Lasanta-Martínez et al., 2005). Decreases
in rural populations, losses of winter pastures in the Ebro
basin and the development of tourism, which partially
replaced agriculture as the main source of revenue, have
led to the breakdown of the transhumance system (= seasonal movement of shepherds and their livestock). This in
turn caused a severe decline in sheep numbers which in
some areas decreased by 90% in the course of the last
century and many summer pastures have become abandoned, particularly those that were less productive and
remote. However, at high altitude in the Pyrenees there
are still large areas of grassland with a very diverse fauna
and flora (Gómez et al., 2003; García-González et al.,
2008). Our study area in the upper part of the Aísa Valley
(western Spanish Pyrenees) is such a biodiversity hotspot
(Isern-Vallverdú, 1990; García-González et al., 1991).
Butterflies are a charismatic and species-rich insect
group. Because they respond rapidly to environmental
* Author for correspondence.
527
Fig. 1. View of the common pastures in the study area (a), Rhamnus pumila (b) and R. alpina (c) host plants of Satyrium spini.
528
changes they are often used as bioindicators (Watt &
Boggs, 2003; van Swaay et al., 2006). The most important biotope for European butterflies, including threatened
species, is grassland (van Swaay et al., 2006). The Bluespot hairstreak, Satyrium spini (Denis & Schiffermüller,
1775), is a monophagous species that in temperate lowlands (Ebert & Rennwald, 1991; Fartmann, 2004; Hermann, 2007) and high mountain ranges (Huemer, 2004) is
associated with species-rich dry grasslands. Although its
host plants (Rhamnus species) are widespread (e.g. Villar
et al., 1997) S. spini is not common in the Spanish
Pyrenees (Abós Castel, 1988; García-Barros et al., 2004;
C. Stefanescu, pers. comm.). Unlike for Central Europe
(Weidemann, 1982; Koschuh et al., 2005; Hermann,
2007) there is no information on the oviposition habitats
of this species in southern Europe (cf. García-Barros &
Fartmann, 2009), which might explain its scattered distribution throughout the Pyrenees.
The aim of this study was to assess the oviposition preferences of the shrub-feeding hairstreak butterfly S. spini
in high mountain common pastures of the Spanish
Pyrenees and recommend a way of managing grasslands
that favours this species. In particular we considered the
following questions:
(i) Which environmental factors determine the egglaying preferences of this species?
(ii) What are the implications for nature conservation in
the light of the ongoing agricultural changes in the Pyrenees?
MATERIAL AND METHODS
Study area
The study area (42°44´N, 0°35´W) is located in the western
Spanish Pyrenees, about 20 km north of Jaca (province Huesca)
in the Aísa Valley. It is approximately 200 ha in size and situated in the high mountain zone (1470–1780 m a.s.l.) in the
eastern part of the Natural Park Valles Occidentales (Sánchez,
2007). The climate is oro-Mediterranean with a mean annual
temperature of 5.5°C, a mean summer temperature of 13.5°C
and a mean winter temperature of –0.6°C (values given for an
altitude of 1780 m a.s.l.). Mean annual precipitation varies with
altitude between 1200 and 2000 mm (Badía Villas et al., 2002).
Within the study area calcareous grasslands used as common
pastures for cattle and sheep dominate. These grasslands developed as a result of livestock husbandry with tree cutting or
burning and replaced native woodlands (García-Ruiz &
Lasanta-Martínez, 1990). The inclinations and aspects of the
hillsides in this valley are very variable. On the steeper slopes
there are large areas of bare rocks and sparsely vegetated screes
(Fig. 1a).
Study species
The Blue-spot Hairstreak, Satyrium spini (Denis & Schiffermüller, 1775), is a lycaenid butterfly with a range extending
from South-west, South and Central Europe to Western Asia. It
is absent from the British Isles, Scandinavia and the oceanic
regions of Central Europe (Ebert & Rennwald, 1991). S. spini
occurs in most parts of the Iberian Peninsula, but mainly in the
mountain ranges (García-Barros et al., 2004). S. spini is a
univoltine species with a flight period ranging from July to
August in the Spanish Pyrenees (Abós Castel, 1988). Females
lay their eggs usually in small batches on various species of
buckthorn (Rhamnus spp.) (Tolman & Lewington, 1998;
TABLE 1. List of the parameters included in the microhabitat
analyses. GLM – Generalized Linear Model, MWU – MannWhitney U test, t – t test.
Variable
Response variable
Host plant occupancy
Egg batches per plant
Predictor variable
Microclimate
Aspect
Sunshine duration (h)1
Vegetation height (cm)3
Shrub layer (< 0.5 m)
Field layer
Vegetation cover (%)3
Shrub layer (< 0.5 m)
Field layer
Mosses/lichens
Litter
Cover of bare ground (%)
Bare soil
Gravel
Stones
Rocks
Total
Host plant cover (%)
Factor levels
Statistical method
2a
GLM (Binomial)
GLM
(quasi-Poisson)
metric
4b
metric
Fisher’s exact test
GLM2, t
metric
metric
GLM4, MWU
GLM, MWU
metric
metric
metric
metric
GLM4, MWU
GLM5, MWU
GLM, MWU
GLM, MWU
metric
metric
metric
metric
metric
metric
MWU
MWU
MWU
MWU
GLM5, MWU
GLM, MWU
1
Accuracy: ¼ h; 2 For most months, values of sunshine duration
were inter-correlated. Therefore the mean of the values for all
the months of a year was used; 3 Height and cover of trees and
taller shrubs were excluded from the analysis as they had zero
values in more than 95% of the samples; 4 Height and cover
were inter-correlated. For GLM analysis, the principal component of both was used; 5 Cover of field layer and total cover of
bare ground were intercorrelated. For GLM analysis, the principal component of both was used; a Occupied = 1, unoccupied =
0; b North = 1, East = 2, South = 3, West = 4.
Koschuh et al., 2005; Hermann, 2007). The larvae spend the
winter within the egg shell and hatch in spring (Ebert & Rennwald, 1991; Hermann, 2007).
Two potential host plants of S. spini occur in the pastures of
the Aísa Valley: Dwarf buckthorn (Rhamnus pumila Turra) and
Alpine buckthorn (R. alpina L. ssp. alpina). R. pumila is a dwarf
shrub with a reptant habit, mostly growing on calcareous rocks
in mountainous regions in Southern Europe (Villar et al., 1997;
Aeschimann et al., 2004). R. alpina is a shrub that can reach 4 m
in height and grows on dry, base-rich and nutrient-poor soils in
the mountains of South-western Europe (Villar et al., 1997;
Aeschimann et al., 2004). On the southern slope of the Pyrenees
both Rhamnus species mainly occur in the high mountain zone
between 1200 and 2500 m a.s.l. (Villar et al., 1997).
Sampling design
In August 2010 we searched both of the potential host plants,
Rhamnus pumila and R. alpina, for eggs of S. spini. We aimed
to sample all aspects within the study area with the same intensity and therefore spent 45 min searching for eggs on north-,
east-, south- and west-facing slopes, respectively. The time
spent searching was measured using a stop-watch, which was on
529
when searching a Rhamnus plant and off when walking to
another plant.
For each host plant that was checked for eggs we noted its
status [with eggs (hereafter referred to as “occupied”) or without
eggs (hereafter referred to as “unoccupied”)], the number of egg
batches found, the number of eggs per batch and several environmental parameters (Table 1). For each egg batch we noted its
position on the host plant and the height above the surface of the
ground (rock or ground). Vegetation structure was recorded in
an area of 50 × 50 cm (hereafter called “microhabitat”) around
each egg batch (Table 1). Potential daily sunshine duration was
recorded for every month of the year using a horizontoscope
(Tonne, 1954). Inclination and aspect were measured using a
compass with inclinometer. The total amount of time spent sampling was one week.
Data analysis
If data were normally distributed (Shapiro-Wilk test) and
variances were homogenous (Levene test), parameters on occupied and unoccupied host plants were compared using a t test.
Otherwise, a Mann-Whitney U test was used. For categorical
variables Fisher’s exact test for small sample sizes was applied.
In addition to this, we used Generalized Linear Models
(GLM) with different response variables (Table 1) for a more
detailed analysis of the R. pumila microhabitats. All explanatory
variables were checked for inter-correlations using Spearman’s
correlation coefficient before being entered into the models.
Principal components were calculated and entered into the
models for variables with correlation coefficients >|0.5|. As our
count data showed overdispersion, we corrected the standard
errors using quasi-Poisson GLMs. Non-significant predictors
were excluded from the final models by stepwise backwardselection using the drop1 command. This command automati-
Fig. 2. Frequency distribution of the number of egg batches
per plant (mean ± SE = 2.9 ± 2.4) (a) and eggs per batch (mean
± SE = 1.4 ± 0.9) (b) (Nbatches = 103; Neggs = 142).
TABLE 2. Mean values ± SD of all numerical environmental parameters on occupied and unoccupied host plants of Satyrium spini
in the Aísa Valley. Comparison of mean or median values was done using t test (t) and Mann-Whitney U test (MWU), respectively;
n.s. = not significant, * P < 0.05, ** P < 0.01, *** P < 0.001.
Rhamnus pumila
Parameter
Microclimate
Sunshine duration (h)
Vegetation height (cm)
Shrub layer (< 0.5 m)
Field layer
Mosses/lichens
Litter
Vegetation cover (%)
Shrub layer (< 0.5 m)
Field layer
Mosses/lichens
Litter
Cover of bare ground (%)
Bare soil
Gravel
Stones
Rocks
Total
Host plant
Height (cm)
Cover (%)
1
R. p. vs. R. a. 1
Occupied
(N = 36)
Unoccupied
(N = 16)
P (test)
Occupied
(N = 11)
P (test)
6.5 ± 1.7
5.1 ± 2.4
*t
6.6 ± 1.7
n.s. t
6.4 ± 13.7
4.1 ± 3.3
0.5 ± 0.7
0.1 ± 0.2
3.4 ± 9.8
4.8 ± 4.3
0.4 ± 0.6
0.3 ± 1.0
n.s. MWU
n.s. MWU
n.s. MWU
n.s. MWU
30.9 ± 13.6
7.8 ± 4.4
0.1 ± 0.2
0.0 ± 0.2
*** MWU
** MWU
n.s. MWU
n.s. MWU
1.5 ± 4.1
16.5 ± 19.2
1.1 ± 1.7
0.4 ± 1.7
2.7 ± 10.0
15.5 ± 20.3
2.7 ± 0.9
0.7 ± 10.0
n.s. MWU
n.s. MWU
n.s. MWU
n.s. MWU
26.4 ± 16.6
27.5 ± 27.3
0.5 ± 1.5
2.7 ± 9.0
*** MWU
n.s. MWU
n.s. MWU
n.s. MWU
1.1 ± 2.2
6.5 ± 11.7
6.1 ± 14.2
51.0 ± 24.1
65.3 ± 22.6
0.2 ± 0.6
4.8 ± 10.0
1.6 ± 2.4
59.5 ± 27.0
66.1 ± 24.7
* MWU
n.s. MWU
n.s. MWU
n.s. t
n.s. MWU
0.9 ± 3.0
29.5 ± 29.4
24.3 ± 34.5
14.1 ± 26.4
71.6 ± 23.4
n.s. MWU
** MWU
* MWU
*** MWU
n.s. MWU
.
16.8 ± 11.2
.
17.7 ± 13.4
.
n.s. MWU
43.2 ± 22.3
31.8 ± 17.5
.
** MWU
Occupied Rhamnus pumila and occupied R. alpina plants were compared.
530
R. alpina
Fig. 3. Polar plot of aspect and slope (°) where Rhamnus host plants grew that were used for oviposition by Satyrium spini (black
symbols) and those that were not (white symbols) (a) and the number of egg batches per Rhamnus pumila plant (b).
cally drops each explanatory variable in turn, and each time
assesses the significance of the dropped variable by likelihood
ratio tests (type III tests). Only explanatory variables significant
at the 5% level were retained in the final models.
Significance tests and correlation analyses were performed
using SigmaPlot 11.0 and GLM analyses were conducted in R
2.12.2 (R Development Core Team, 2011).
RESULTS
In total we surveyed 52 R. pumila (36 occupied vs. 16
unoccupied) and 13 R. alpina plants (11 vs. 2) (Table 2).
Altogether we found 103 egg batches on 36 R. pumila
and 40 on 11 R. alpina (Fig. 2, Table 2). Usually, occupied host plants had one up to three batches (75% of the
cases); four to twelve batches per host plant rarely
occurred (25%) (Fig. 2). Females usually laid their eggs
singly (76%) or in small groups of two or three eggs
(22%). Egg batches of four to eight eggs were rare exceptions (2%). Mean size of the egg batches did not differ
between R. pumila (mean ± SD = 1.4 ± 0.9) and R. alpina
(mean ± SD = 1.5 ± 0.9) (Mann-Whitney U test: U =
1881.0, P = 0.30). Eggs were deposited on twigs and in
twig forks. Due to its reptant growth, batches on
R. pumila were always situated very close to the surface
of the ground (mean ± SD = 2.0 ± 2.1 cm). Eggs on
R. alpina were found from 1 to 57 cm above ground with
three quarters of them between 5 and 15 cm (mean ± SD
= 10.5 ± 10.0 cm). Eggs were laid at significantly different heights on the two host plants (Mann-Whitney U
test: U = 445.5, P < 0.001).
Typically, the microhabitats of occupied R. pumila
were very sunny and sparsely vegetated rocks, solitary
boulders or screes in the pastures (Fig. 1b, Table 2). The
sites were dominated by bare rocks and vegetation usually covered less than one fifth of the ground. Microhabitats of occupied R. pumila were – compared to
unoccupied ones – characterized by a significantly longer
sunshine duration and cover of bare soil. Microhabitats of
occupied R. alpina had similar characteristics and were
mostly found on screes and river banks (Fig. 1c, Table 2).
However, shrub height and cover, field layer height, hostplant cover and the cover of gravel and stones were significantly higher, while that of rocks was significantly
lower.
Although occupied plants of both Rhamnus species
were found in areas with a wide range of aspects and
inclinations, most occupied R. pumila occurred on east-,
south- and west-facing slopes (Fig. 3a, Table 3). This difference in aspect between occupied and unoccupied R.
pumila plants was slightly not significant (P = 0.06).
However, the number of batches per R. pumila plant was
TABLE 3. Absolute and relative frequencies of the nominal
variable aspect in occupied and unoccupied Rhamnus pumila
microhabitats. Results of Fisher’s exact test using absolute frequencies: occupied vs. unoccupied: P = 0.06; number of egg
batches vs. unoccupied: P < 0.001.
Aspect
North
East
South
West
Occupied
(N = 36)
Unoccupied
(N = 16)
Egg batches
(N = 103)
N
%
N
%
N
%
6
9
12
9
16.7
25.0
33.3
25.0
9
2
3
2
56.3
12.5
18.8
12.5
9
23
44
27
8.7
22.3
42.7
26.2
531
TABLE 4. Results of the Generalized Linear Model analysis
used to determine the association of several environmental
parameters (predictor variables, Table 1) with the presence of
egg batches in Rhamnus pumila microhabitats (a) and the
number of egg batches per R. pumila plant (b). Non-significant
predictors were excluded from the final model by stepwise
backward selection (P > 0.05). Sample sizes: 36 occupied
microhabitats, 16 unoccupied microhabitats, 103 egg batches.
Estimate
Variable
a) Presence of egg batches
Sunshine duration
SE
Z
P
0.030 0.014 2.213 < 0.05
2
Pseudo R [Nagelkerke’s] = 0.14
b) Egg batches/plant
Sunshine duration
0.021 0.007 2.930 < 0.01
Pseudo R2 [Nagelkerke’s] = 0.36
significantly higher on plants in those aspects than on
north-facing slopes (Fig. 3b, Table 3).
The importance of unshaded sites that receive large
amounts of direct solar radiation is confirmed by the
results of the GLM analyses (Table 4). Potential daily
sunshine duration was the only significant parameter
explaining the presence of egg batches on R. pumila
[Pseudo R² (Nagelkerke’s) = 0.14] and the number of egg
batches per R. pumila plant [Pseudo R² (Nagelkerke’s) =
0.36].
DISCUSSION
This study on the oviposition habitats of S. spini in high
mountain common pastures of the Spanish Pyrenees
showed that females used R. pumila and R. alpina for oviposition. Both species represent novel host plant records
for Spain (cf. Munguira et al., 1997). Occupied plants
grew mostly at sparsely vegetated grassland sites with
large patches of bare rocks, stones or gravel. Most of the
egg batches were laid close to the ground, on the reptant
R. pumila directly above the rock surface (mostly < 2 cm)
and on the taller R. alpina mostly within 15 cm above
ground. In three quarters of the cases the batches contained only one egg. The number of batches per R. pumila
plant was highest on east-, south- and west-facing slopes
and least on north-facing slopes. Presence of eggs and the
number of egg batches per R. pumila plant were best
explained by a long sunshine duration.
These findings indicate that a warm microclimate is of
crucial importance for S. spini. Although the two host
plants of S. spini have completely different growth forms,
all egg-laying sites exhibit roughly the same characteristics that ensure favourable microclimatic conditions.
Based on the results of this study we conclude that there
are three main factors that contribute to the relatively high
temperatures in the oviposition habitats of S. spini:
(i) By preferring sunny locations on east-, south- and
west-facing slopes, females make sure that the eggs and
larvae receive large amounts of direct solar radiation.
532
(ii) Large patches of bare ground around the host plants
further warm up the near-ground air layer (cf. Stoutjesdijk & Barkman, 1992).
(iii) The eggs are laid close to the ground in the
boundary layer where wind speed is lowest and air temperatures are highest (cf. Porter, 1992).
The importance of a warm microclimate for the immature stages has been described for many thermophilous
butterfly species (García-Barros & Fartmann, 2009) and
has already been shown for S. spini in Central European
lowlands and low mountain ranges (Koschuh et al., 2005;
Hermann, 2007; Löffler et al., 2013). In our study area,
however, warm microhabitats are likely to be even more
important than in Central Europe. At the lower altitudes
in Central Europe, where the climate is mild (Ellenberg &
Leuschner, 2010), this species lays its eggs at heights of
up to 1.3 m above the ground and the occurrence of bare
ground, rocks or gravel is not a prerequisite for egglaying (Löffler et al., 2013). We assume that the preference for unusually warm microhabitats is explained by
the harsh climatic conditions near its altitudinal range
limit in the Pyrenees. The growing season is rather short
with 80–150 days (Aldezabal Roteta, 2001), and the mean
summer temperature of 13.5°C is relatively low (given for
an altitude of 1780 m a.s.l.) (Badía Villas et al., 2002).
Some other studies also indicate that butterflies compensate for the cooler climate near their cool range margins
by occupying relatively narrow and hot niches (Thomas,
1993; Thomas et al., 1998; Merrill et al., 2008).
S. spini is known to deposit its eggs usually in small
batches (Hermann, 2007). Koschuh et al. (2005) and Löffler et al. (2013) showed for low mountain ranges in
Eastern Austria and lowlands in Central Germany,
respectively, that 25% of the batches consisted of one egg
and 75% of two or more eggs. Surprisingly, in our study
the ratio was reversed with 76% of the eggs laid singly.
Dispersing the eggs in space rather than concentrating
them in a few localities has often been considered as a
strategy of risk-spreading (García-Barros & Fartmann,
2009). In line with this, we interpret the oviposition of
single eggs by a female in our study area as a strategy to
increase the survival rate of the offspring under unfavourable and poorly predictable climatic conditions. The climate in the high mountain zone of the Spanish Pyrenees
is characterised by relatively short and cool summers,
long and cold winters (see above), high velocity winds in
winter causing snowdrift and damaging the vegetation
(pers. observ.) and an overall large inter-annual variation.
In contrast, weather conditions at the lower altitudes in
Central Europe are not as harsh and more predictable. For
Hamearis lucina, small egg batches are also thought to
constitute a risk-spreading strategy to cope with unfavourable climatic conditions along a geographic gradient
(Anthes et al., 2008). However, to verify this assumption
it is necessary to undertake further studies on batch size
and survival rates of S. spini eggs and larvae along a climatic gradient.
Implications for conservation
Based on the results of this study we conclude that the
preservation of open grasslands with small buckthorn
plants growing in very sunny and warm locations is crucial for the long-term survival of S. spini. Abandonment
of common pastures in the Spanish Pyrenees with subsequent shrub encroachment and reforestation would lead to
shading of the host plants and a loss of habitat for S. spini
(cf. Löffler et al., 2013) and probably many other thermophilous grassland species (Steffan-Dewenter & Tscharntke, 2002; WallisDeVries et al., 2002; Stefanescu et al.,
2011). Areas above the climatic timberline might be too
cold and suitable habitats at lower elevations in the
Pyrenees, where the opposed processes of agricultural
intensification and abandonment are even more accentuated than in high mountain areas (García-Ruiz & LasantaMartínez, 1990; Lasanta-Martínez et al., 2005), are
probably scarce. Sites where the vegetation structure
remains open without any kind of management (e.g.
floodplains, extremely steep slopes) are few in number
and mostly of small size (pers. observ.).
The best way to maintain an open landscape and preserve the species-rich and structurally diverse vegetation
of the high mountain common pastures is the traditional
combination of sheep and cattle grazing. Sheep are
known to be selective grazers and have a homogenising
effect on the vegetation (Rook et al., 2004), but also contribute to the maintenance of some specific plant species
and communities of high conservation value (Sebastià et
al., 2008). Cattle in contrast do not select particular plant
species and thus, enhance vegetation heterogeneity
(Sebastià et al., 2008) and are effective in controlling
shrub encroachment even at moderate stocking densities
(Casasús et al., 2007). Several recent studies have documented positive effects of cattle grazing on species richness of plants and insects (e. g. Pykälä, 2003; Pöyry et al.,
2004; WallisDeVries et al., 2007). Besides, cattle are the
farm animals preferred by local farmers for economic reasons (García-Ruiz & Lasanta-Martínez, 1990) and if conservation policies are to be effective they should be based
on economically profitable measures. Where livestock
grazing alone is not sufficient to counteract reforestation,
mechanical removal of shrubs and trees should be done
like in former (and partially recent) times, when woody
species were cut by farmers for firewood and in order to
keep the pastures open.
ACKNOWLEDGEMENTS. We would like to thank G. Hermann, M. Konvicka and two anonymous reviewers for valuable
comments on an earlier version of the manuscript.
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Received February 29, 2012; revised and accepted April 26, 2012